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Landscapes Forest and Global Change - ESA - Escola Superior ...

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A.L. Teixido et al. 2010. Impacts of changes in l<strong>and</strong> use <strong>and</strong> fragmentation patterns on Atlantic coastal forests<br />

434<br />

Table 2: L<strong>and</strong>scape metrics of forest in Fragas do Eume Natural Park in 1957 <strong>and</strong> 2003. The absolute <strong>and</strong><br />

relative change of each l<strong>and</strong>scape metric is also shown. <strong>Change</strong> values greater than 0 indicate gains, <strong>and</strong><br />

those less than 0 indicate losses<br />

L<strong>and</strong>scape metric 1957 2003 <strong>Change</strong> 1957-2003<br />

Absolute Relative (%)<br />

Largest patch index (%) 32 11 -22 -34.4<br />

Mean patch size ± SD (ha) 52 ± 344 19 ± 110 -33 -63.5<br />

Total edge length (km) 367 484 +118 +32.1<br />

Total core area (ha) 2,054 1,178 -876 -42.6<br />

Largest patch core area (ha) 1,842 530 -1312 -71.2<br />

Mean distance ± SD (m) 489 ± 315 641 ± 546 +152 +31.1<br />

number of patches under 10 ha, <strong>and</strong> particularly those under 1 ha, increased from 1957 to 2003<br />

<strong>and</strong> represented a higher proportion of the total number of patches.<br />

There was an increase in total edge length <strong>and</strong> a decline in total core area <strong>and</strong> also a decline in<br />

largest patch core area. Mean distance among patch edges increased 31%. <strong>Forest</strong> patches also<br />

showed an increase of 32% in the total adjacency index between 1957 <strong>and</strong> 2003 (Table 2).<br />

In 1957, a large proportion (89%) of total water course length was covered by riparian forests,<br />

including the whole length of the Eume River (Fig. 2). In 2003, riparian forest length decreased<br />

34%. Losses were associated to eucalypt plantations (11%), <strong>and</strong> mostly to the building of the<br />

water reservoir (23%).<br />

Figure 2: <strong>Change</strong>s in the spatial distribution of riparian forest in Fragas do Eume Natural Park<br />

4. Discussion<br />

Our results showed a high spatial heterogeneity in l<strong>and</strong> cover over the whole area in both study<br />

periods, with most l<strong>and</strong> cover classes consisting of a large number of patches interspersed with<br />

other different classes (Fig. 1). L<strong>and</strong> cover area comparisons <strong>and</strong> detailed transition analyses<br />

showed that the l<strong>and</strong>scape was highly dynamic over the 50-year period, mostly due to<br />

intensification of exotic species plantations (especially eucalypt), farming ab<strong>and</strong>onment <strong>and</strong> the<br />

building of a water reservoir. Eucalypt plantations were mostly introduced in northern Spain<br />

during the second half of the 20th century because of their high pulp productivity. Farming<br />

ab<strong>and</strong>onment also represented large l<strong>and</strong>scape changes due to depopulation of these rural<br />

lowl<strong>and</strong>s during the second half of the 20th century (Calvo-Iglesias et al. 2006).<br />

<strong>Forest</strong> <strong>L<strong>and</strong>scapes</strong> <strong>and</strong> <strong>Global</strong> <strong>Change</strong>-New Frontiers in Management, Conservation <strong>and</strong> Restoration. Proceedings of the IUFRO L<strong>and</strong>scape Ecology<br />

Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.)<br />

2010, Instituto Politécnico de Bragança, Bragança, Portugal.

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